Next Article in Journal
Building Energy Savings by Developing Complex Smart Windows and Their Controllers
Next Article in Special Issue
Microorganisms Isolated from Saharan Dust Intrusions in the Canary Islands and Processes of Mineral Atmospherogenesis
Previous Article in Journal
Principal Hugoniots of Promethium, Terbium, Thulium, Lutetium, and Actinium in a Wide Pressure Range
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

The Marine Bacterial Genus Euzebya Is Distributed Worldwide in Terrestrial Environments: A Review

by
Jose Luis Gonzalez-Pimentel
1,
Tamara Martin-Pozas
2,
Valme Jurado
3,
Leonila Laiz
3,
Angel Fernandez-Cortes
4,
Sergio Sanchez-Moral
2 and
Cesareo Saiz-Jimenez
3,*
1
Centro Andaluz de Biologia del Desarrollo (CABD, UPO-CSIC-JA), Facultad de Ciencias Experimentales, Departamento de Genetica, Universidad Pablo de Olavide, 41013 Sevilla, Spain
2
Museo Nacional de Ciencias Naturales, MNCN-CSIC, 28006 Madrid, Spain
3
Instituto de Recursos Naturales y Agrobiologia, IRNAS-CSIC, 41012 Sevilla, Spain
4
Departamento de Biologia y Geologia, Universidad de Almeria, 04120 Almeria, Spain
*
Author to whom correspondence should be addressed.
Appl. Sci. 2023, 13(17), 9644; https://doi.org/10.3390/app13179644
Submission received: 2 June 2023 / Revised: 10 August 2023 / Accepted: 23 August 2023 / Published: 25 August 2023
(This article belongs to the Special Issue Geomicrobiology: Latest Advances and Prospects)

Abstract

:
The advent of molecular tools, and particularly next-generation sequencing, has dramatically changed our knowledge of the diversity of microbial life on Earth. In recent decades, many studies on different terrestrial environments have described the intriguing diversity and abundance of Euzebyales/Euzebyaceae/Euzebya, yet its role in the geochemical cycle of elements is unknown. In addition, as far as we know, no Euzebya isolates have been obtained from terrestrial niches. In this review, it is shown that Euzebya and other haloalkaliphilic bacteria can thrive under harsh conditions, such as high concentrations of sodium and/or calcium, high electric conductivity and alkaline pH, highly variable temperatures, and water fluctuations. These conditions are quasi-extreme in the studied terrestrial environments. However, the culture media used so far for isolation have failed to reproduce the original conditions of these terrestrial ecosystems, and this is likely the reason why strains of Euzebya and other bacteria that inhabit the same niche could not be isolated. It is expected that culture media reproducing the environmental conditions outlined in this review could cope with the isolation of terrestrial Euzebya and other haloalkaliphilic genera.

1. Introduction

In terms of microbial diversity, the oceans represent the largest biosphere habitat, containing about 70% of the prokaryotic biomass [1]. In recent decades, interest in the bioactive compounds from marine bacteria has grown enormously [2,3,4,5,6,7,8], and many works have focused on rare marine Actinomycetota [9,10,11,12,13]. One of the most intriguing and rare genera of marine Actinomycetota is Euzebya. No terrestrial Euzebya has been isolated so far.
The genus Euzebya was described by Kurahashi et al. [14] to accommodate a Gram-positive actinobacterial strain isolated from the epidermis of Holothuria edulis, a sea cucumber collected in the Sea of Japan. The strain was characterized by a reddish-orange or tangerine color and was able to grow in sodium chloride concentrations of 0.5–12%, but no growth was observed in the absence of sodium chloride or at a concentration of 15%. Optimal growth temperatures were in the range of 20–28 °C and pH 7–9. No growth was obtained at pH 6 or 10. The type strain is Euzebya tangerina from the new order Euzebyales and the new family Euzebyaceae [14]. A second member of the genus, Euzebya rosea, was isolated from the waters of the East China Sea and showed a light pink color, optimal growth at 25–30 °C, and pH 6–7. Optimal sodium chloride concentrations were 1–4% [15].
Euzebya pacifica was the third species of the genus, isolated from seawater collected at 150 m depth in the Eastern Pacific Ocean [16]. Colonies were pink, with optimal growth at 30–35 °C, in sodium chloride concentrations of 1–2%, and pH 6.5. This last species could grow in the absence of sodium chloride. The complete genome sequence of E. pacifica revealed its ecological roles in marine carbon, nitrogen, phosphorus, and sulfur cycles [17]. In general, the three marine species of Euzebya are characterized by their tolerance to relatively high sodium chloride concentrations, growth at neutral pH (7), and temperatures from 20 to 35 °C.
The advent of molecular tools, particularly next-generation sequencing (NGS), has dramatically changed the knowledge of the diversity of microbial life on Earth. In recent decades, many studies on different terrestrial environments, including caves [18,19,20,21,22,23,24,25,26,27,28,29,30,31,32,33,34,35,36], have described the diversity and abundance of Euzebyales/Euzebyaceae/Euzebya; however, as far as we know, no Euzebya isolates have been obtained from terrestrial niches. This prompted us to review the habitats where Euzebya sequences were found and their ecological requirements in order to understand the failures in the adoption of isolation protocols that led to the lack of terrestrial isolates. The diversity and abundance of Euzebyales/Euzebyaceae/Euzebya in most terrestrial environments are intriguing and its role in the geochemical cycle of elements is unknown, and thus the isolation of Euzebya strains could help to understand why this abundant bacterial genus is distributed worldwide, even in extreme environments.

2. Metagenomic Detection of Euzebya in the Environment: Caves

Caves are mineral environments, often oligotrophic in nature. Rocks, speleothems, and mineral deposits, such as moonmilk, are colonized by microbial communities, which develop as colored biofilms [18,19,20]. To our knowledge, the first report on the occurrence of Euzebya in caves was in a study by Cuezva et al. [18]. In Altamira Cave, Spain, sequences with 82–92% similarity to the nearest relative Euzebya tangerina were retrieved from grey biofilms, suggesting that they probably represented an unknown species. Euzebya represented 72.8% of the clones retrieved from the grey biofilms [18]. Riquelme et al. [19] recovered representatives of Euzebyales from colored microbial mats found in volcanic caves in the Azores, Hawai’i, and New Mexico, and stated that the different clades obtained suggested a significant diversity within the sequences found. Other papers reported Euzebya sequences from caves in different geographical regions [21,22,23,24,25,26,27,28,29,30,31,32,33,34,35,36] (Table 1).
The composition of microbial communities was found to be dependent on geochemical and microclimatic parameters. In this context, Frazier [29] reported the high relative abundance of Euzebya (up to 30.7%) in one cave and its negligible occurrence (up to 0.2%) in another cave from mineralogically similar formations located 65 km apart. The difference in abundance was attributed to flooding and clay deposition in the Euzebya-rich cave. Also interesting was the abundance of Euzebyaceae in pink biofilms from Pindal Cave, Spain (7.0–16.0%), coincident with the pink color of the three described Euzebya species [36].
A recent study was conducted on the biofilms present in Covadura Cave, located in the gypsum karst of Sorbas, Almeria, Spain. The karst comprises over 100 km of passages within the six most important caves (Covadura Cave, GEP Complex, C3 Cave, Gypsum Cave, Treasure Cave, and Water Cave), which are subject to condensation–dissolution mechanisms. Water condensation on the cooler walls of Covadura Cave takes place mainly during the dry period (July to October) and the biofilms show water droplets on their surface. Biofilm proliferation has been associated with the strong condensation existing in some caves [36], as condensation favors the colonization of cave walls by microorganisms [18,19].
The data revealed that Euzebyaceae were abundant in Covadura Cave white biofilms collected in 2010, but their relative abundance was drastically reduced in the 2022 sampling (Table 1). This could be associated with the severe droughts, the last of which occurred between 2017 and 2018, and which continue until now. In the yellow biofilms, the decrease in abundance was lower.
Euzebya was also abundant in volcanic caves. The genus was found in caves in the Azores, Canary Islands, Galapagos, Hawai’i, Idaho, Tennessee, and Mexico [19,20,24,26,28,29,30,34]. Gonzalez-Pimentel et al. [24] stated that yellow biofilms from a cave on the Canary Island of La Palma were dominated by metabolically active Euzebya (43.9% RNA clones vs. 26.0% DNA clones). In the other three La Palma caves [26], the relative abundance of Euzebya was lower (Table 1).
La Palma caves are characterized by the leaching of dissolved organic matter from the soil surface, and its transport inside the cave is favored by the low thickness and high porosity of the volcanic rock [37]. Euzebya colonizes the mineral formations and deposits in caves, usually at an alkaline pH (8–10), where it develops as biofilms of different colors. The wide distribution in karstic, volcanic, and gypsum caves all over the world indicates that terrestrial Euzebya can thrive in these humid, largely mineral environments [38].

3. Euzebyales in Extreme Environments

Saline and hypersaline terrestrial environments include salt mines, sediments of desiccated salt lakes, saline and alkaline soils, salt marshes, etc. These environments often have salt concentrations higher than that of seawater and support halophilic microorganisms that have adapted to deal with extreme environmental parameters (high salt concentrations, temperatures, and pH), although their community composition and structure vary depending on salinity fluctuations in the environment [39].
The occurrence of Euzebya in these environments has been reported in numerous studies [40,41,42,43,44,45,46,47,48,49,50,51,52,53,54,55], denoting the ability of the members of this genus to prosper in habitats with high salt concentrations (Table 2).
Interestingly, the wide occurrence of Euzebya and its haloalkaliphilic relatives has been registered in the drained sediments of former Mexican lakes (Texcoco and Rincon de Parangueo) [40,45], and the Songnen Plain of Northeast China, one of the three regions with extensive saline–sodic soils in the world [50,51,52,53].
The Texcoco Lake sediments are characterized by a very high pH (10) and an electric conductivity (EC) of up to 179.8 dS m−1 [40,42,44]. There, Euzebya was one of the dominant bacterial genera with relative abundances >10% [42]. It has been reported that organic carbon additions to the sediments increased Euzebya abundance [42].
In the Songnen Plain of Northeast China, with very high pH (>10) and high EC, Euzebya showed high relative abundance [50,52], as well as a high sodicity/salinity niche preference, however, the genus was depleted or absent when sodicity/salinity decreased [51].
In other highly saline environments, such as salt marshes, mines, and lake soils, Euzebya was detected in the rhizosphere of halophytic plants [41,43,47,48,49,54].
Chen et al. [56], using comparative genomics, investigated the salt adaptation mechanism of species within the class Nitriliruptoria, including Euzebya tangerina and E. rosea. They showed that the Nitriliruptoria species possess specific salt tolerance mechanisms.
Deserts, covering around 33% of the planet’s surface, have been explored in search of extremophilic and extremotolerant Actinomycetota producing novel bioactive compounds [57,58,59,60]. However, the use of molecular tools (next-generation sequencing) revealed dominant members of the extremophilic microbial communities that have not been yet isolated. They included Euzebya, both in cold environments (Antarctica) and hot deserts (Atacama, Sahara, Colorado Plateau, etc.) [61,62,63,64,65,66,67,68,69,70,71,72] (Table 2).
Table 2. Occurrence of Euzebyales/Euzebyaceae/Euzebya in extreme environments.
Table 2. Occurrence of Euzebyales/Euzebyaceae/Euzebya in extreme environments.
LocationTaxaType of Sample References
Saline and hypersaline environments
Texcoco, MexicoEuzebyaSoil[40]
Dafeng, Jiangsu, ChinaEuzebyaSoil/Rhizosphere[41]
Texcoco, MexicoEuzebyaSoil[42]
Khewra salt mines, PakistanEuzebyaSoil/Rhizosphere[43]
Texcoco, MexicoEuzebyaSoil[44]
Rincon de Parangueo, MexicoEuzebyalesSediment[45]
Rincon de Parangueo, MexicoEuzebyaSediment[46]
Chaka Salt Lake, ChinaEuzebyaRhizosphere[47]
Jeddah, Saudi ArabiaEuzebyaSoil/Rhizosphere[48]
Lebrija, Seville, SpainEuzebyaSoil/Rhizosphere[49]
Songnen Plain, Jilin, China EuzebyaSoil[50]
Songnen Plain, Jilin, China EuzebyaSoil[51]
Songnen Plain, Jilin, China EuzebyaSoil[52]
Songnen Plain, Jilin, China EuzebyaSoil[53]
Daqing, Heilongjiang, China EuzebyaSoil/Rhizosphere[54]
Hisar, Haryana, IndiaEuzebyaSoil[55]
Cold and hot deserts
Victoria Valley, AntarcticaEuzebyaRocks[58]
Atacama DesertEuzebyaRocks[59]
McMurdo Dry Valleys, AntarcticaEuzebyalesSoil[60]
McMurdo Dry Valleys, AntarcticaEuzebyaceaeSoil[61]
Australia/Northern AntarcticaEuzebyaSoil[62]
Cabo de Gata, Nijar Natural Park, SpainEuzebyaceaeSoil[63]
North-Central AlgeriaEuzebyaSoil/Rhizosphere[64]
Eastern Pamir, TajikistanEuzebyaceaeRocks/soil crusts[65]
Mackay Glacier region, Antarctica EuzebyalesSoils[66]
Colorado Plateau Desert, USAEuzebyaSoil[67]
Northwest deserts of ChinaEuzebyaSoil[68]
Gurbantunggut Desert, Xinjiang, China EuzebyaSoil/Rhizosphere[69]
Euzebya was one of the most frequently detected genera in Australian and Northern Antarctica soils. There, Actinomycetota diversity increased with increasing pH and sodium concentration, and this applies particularly to Euzebya [65].
The McMurdo Dry Valleys is the largest ice-free soil region in Antarctica. There, Euzebyales were abundant only in the soil samples with moisture below 6.82% but largely declined or were absent in the soil with moisture content above 15.57% [63]. In Victoria Valley, within McMurdo Dry Valleys, two families, Euzebyaceae and Rubrobacteraceae, were abundant (over 30%) in endolithic niches and less frequent in soils. It has been reported that water availability largely conditioned the distribution of these actinobacterial families [64].
In Antarctica, the rock-inhabiting microbial communities are dominated by Cyanobacteria and Actinobacteria, particularly Euzebya, which also occupy hypolithic niches [63]. In the cold mountain desert of Eastern Pamir in Tajikistan, Euzebya was present both in rocks (endolithic) and in biological soil crusts [68].
In addition, Euzebya was found in endolithic niches in the hyperarid zone of the Atacama Desert, Chile [62], and in soils from the Sahara, Colorado Plateau, and China [67,70,71,72].

4. Euzebyales in Soils and Other Diverse Environments

Table 3 shows the occurrence of Euzebya in agricultural and contaminated soils, and other diverse environments [73,74,75,76,77,78,79,80,81,82,83,84,85,86,87,88,89,90,91,92,93,94,95,96,97,98,99,100,101,102,103,104,105,106,107,108,109,110,111,112,113,114,115,116,117,118,119].
Euzebya was found in the rhizosphere of Agave lechuguilla in the saline and oligotrophic soils of Cuatro Ciénegas Basin, Mexico [76,81], as well as in other plant rhizospheres from different regions [73,75,79,81,85,91,92,95].
Euzebya is represented in soils all over the world [74,77,78,80,82,83,84,86,89,90,93,94]. Several authors have reported the occurrence of Euzebya in clean and healthy soils and its absence in polluted soils [77,96,97]. However, Euzebya has also been found in bauxite residue disposal areas and copper mine wastes [98,99,100,101].
The presence of Euzebya has been recorded in saltern and salt lakes, terrestrial and sea waters, marine organisms [103,104,105,106,107,111,113,119], bentonite [110], animals [112,114,115], and humans [116,117,118]. In addition, the genus was found on a sandstone surface, covered by efflorescences, at the Wawel Royal Castle in Poland [108]. In a report on the microbial communities of efflorescences from Roman tombs in the Carmona Necropolis, Spain, a high number (60%) of clones showing a similarity of 87% with the genus Nitriliruptor were retrieved. At the time of this study, 2009 [102], no Euzebya species had been described. However, a further study [26] showed that these clones had 92.5% similarity with Euzebya tangerina, while an updated revision of these clones showed a similarity of 91.7–92.7% with Euzebya pacifica.

5. Relationship of Euzebyales with Other Members of Microbial Communities in Diverse Environments

A review of all the reports available in the literature provided some insights into the relationship of Euzebya with other taxa in different environments. In fact, several taxonomic groups may inhabit the same niche as Euzebya. Thus, Euzebya is present in most caves together with Crossiella, Rubrobacter, wb1-P19 (Nitrosococcales), and Gaiella, among other genera [19,21,23,27,28,29,33,34,35,36]. Caves are characterized by high relative humidity, in most cases near saturation, high mineral concentration, mainly of calcite in karstic and basaltic rocks in volcanic caves, as well as alkaline pH. In some pristine caves, oligotrophy is an environmental constraint.
In saline and hypersaline environments, the order Euzebyales is accompanied by other orders common to these extreme environments, such as Nitriliruptorales, Rubrobacterales, Solirubrobacterales, Gaiellales, Acidimicrobiales, Oceanospirillales, Rhizobiales, KSA1 (Bacteroidetes), etc. [41,42,45,49,50,51,52,53]. Most members of these orders require high pH and salt concentrations, and oligotrophy is common in these environments. There are a few outstanding reviews on heavy metal resistance in halophilic Bacteria and Archaea [120,121,122]. These and other studies [123,124] revealed that the mechanism of heavy metal resistance is associated with salinity tolerance and an increase in salinity and pH-enhanced tolerance to toxic metals. Nitriliruptoria species possess salt tolerance mechanisms [56] and it is likely that heavy metal resistance could also be attributed to Euzebya.
In deserts, Euzebya has been found together with Nitriliruptor, Rubrobacter, Solirubrobacter, Gaiella, Halomonas, etc. [62,64,65,68,69,70,71]. Water availability is scarce in deserts and environmental conditions become more challenging (e.g., strong oligotrophy and high mineral deposits). Most of these genera are known for their ability to resist extreme desiccation, high UV and ionizing radiation, temperature fluctuations, and high salinity and metal concentrations [62]. In addition, the pink color of most species of these genera is due to the presence of bacterioruberin, a carotenoid pigment with UV-protective properties. It is suggested that Euzebya may possess most of the above-described characteristics, although as far as we know no pigment identification has been reported for any of the three marine species.
In soils, the co-occurrence of Euzebyales with Nitriliruptorales, Rubrobacterales, Solirubrobacterales, Gaiellales, Oceanospirillales, Rhizobiales, etc., is frequently reported [84,86,87,88,89], as previously stated for caves, saline, hypersaline, and desert environments.
To summarize, some microbial lineages present in harsh terrestrial environments show successful adaptation strategies and the ability to cope with available scarce nutrient sources in unfavorable climatic and geochemical conditions.

6. Culture Media for the Isolation of Euzebya in Terrestrial Environments

From 90 papers reporting the occurrence of Euzebya in different environments (Table 1, Table 2 and Table 3), only 13 described the isolation of bacteria, but only three marine species of Euzebya were successfully isolated on marine culture medium with 1–2% of sodium chloride, pH near 7, and at a temperature of 25 °C [14,15,16].
The terrestrial environments where Euzebya have been found are characterized by haloalkaliphilic conditions, high pH (9–10), and high to moderate salt contents. The availability of water in these ecosystems is widely variable, from dry conditions to 100% relative humidity, which suggests the great adaptability of this genus. In addition, the range of mean temperatures of these environments is highly variable, from −30 °C (winter in McMurdo Dry Valleys) to >40 °C in deserts, with large daily temperature fluctuations in each location.
The culture media used by different authors contained a wide array of carbon and nitrogen sources (peptone, tryptone, starch, tyrosine, glycerol, asparagine, sodium caseinate, malt extract, humic acid, glucose, oatmeal, etc.), mainly used for the isolation of Actinomycetota. At the same time, the media rarely contained high concentrations of salts (sodium or calcium), and the pH was not adjusted to the alkalinity ranges where terrestrial Euzebya and other related bacteria are abundant. None of these attempts were able to isolate strains of Euzebya, Nitriliruptor, Rubrobacter, Solirubrobacter, Gaiella, Halomonas, etc., which clearly indicates that the culture media used failed to reproduce the ecological conditions where these bacteria succeed.
As a matter of fact, Rubrobacter strains were isolated from biodeteriorated Roman tombs and a church with abundant efflorescences using media developed for halobacteria (DSMZ media 372, 1018, 1350) [125]. Three of these strains represented a new species, Rubrobacter bracarensis, that grew on tryptone soya agar (TSA) with concentrations of 30% NaCl, with an optimum at 3–10%, in contrast to other described species of Rubrobacter, which did not grow at concentrations above 5–6% NaCl [126]. This proves that culture media mimicking the original ecological conditions can provide novel, not yet cultured strains.

7. Attempts to Isolate Euzebya from Pindal Cave

Pindal Cave is a shallow limestone cave formed through epigenic processes and located very close to the surface. The cave is 590 m long and due to the geographical location has a humid oceanic climate. The cave has a stable annual temperature (11.6 °C) with only minor fluctuations throughout the year (<2 °C/year). This cave is well-ventilated with relatively low annual average values of CO2 (680 ppm) and radon (950 Bq/m3) [36].
In Pindal Cave, pink biofilms primarily develop on the surface of calcite speleothems in areas near the entrance and Euzebyaceae reached a relative abundance of 7–16% (Table 4); the biofilms have a rough surface and are formed by aggregates of cells, mostly rounded, with extensive filaments (Figure 1). Other abundant genera were Crossiella and wp1-P19. The ecological significance of the five top taxa in Pindal Cave was discussed elsewhere [36,127,128]. However, attempts to isolate Euzebya using different culture media failed. The following media were used: nutrient agar (NA), B-4 medium [129], GYM Streptomyces medium (DSMZ 65), Dimethylsulfone medium [130], TSA, diluted TSA/1000, and TSA supplemented with NaCl (3%) and MgSO4·7H2O (2%) (DSMZ 1350) [125]. In all these media, the pH was near 7, and not as markedly alkaline as Euzebya requires (pH 9–10), as denoted by their habitats; in other cases, the absence of relatively high NaCl concentrations likely prevented its isolation.
A culture-dependent approach revealed 33 isolates representing 19 identified species, as listed in Table 5. The isolates were affiliated with the phyla Actinomycetota (three genera) and Bacillota (five genera). Both phyla are widespread in nature [131,132,133,134] and the genera isolated from pink biofilms were spore-forming bacteria. Remarkably, none of the bacteria isolated were representatives of the top major taxa recovered by NGS (Table 4). In fact, NGS of the pink biofilm revealed only Streptomyces with a relative abundance of 0.01%, which was also isolated on culture media. The results indicated significant differences in the bacterial communities detected in the pink biofilm when applying these two different approaches.
The inability of culture-dependent and independent methods to detect the same bacterial species has already been reported [135,136]. Laiz et al. [137] stated that culture-dependent techniques lead to an overestimation of the spore-forming bacteria, as shown in Table 5. They found that the apparent abundance of these bacteria can be explained by the fast growth of spores in the plates.
The failure in obtaining Euzebya isolates prompted us to review the ecological niches where Euzebya can be found. The survey revealed that the environmental conditions requested by Euzebya were not met in the culture media used thus far.
Culture media reproducing the environmental conditions outlined in this review, e.g., marine agar and SN medium (including 1/10 dilutions of these media), pH 9–10, and sodium chloride concentrations around 3% or more, could allow the isolation of terrestrial Euzebya and other haloalkaliphilic genera. Marine agar and SN medium [138] have been used for the isolation of marine Euzebya [14,15,16]. Alternatively, for maintaining a high pH, the medium Z8-NK, as described by Flores et al. [139], R2A, and/or other media with the addition of trace elements, amino acids, vitamins, and simple carbon sources to a minimal culture medium should be explored.

8. Concluding Remarks

NGS technologies have allowed the detection of unknown microorganisms and extended our knowledge of the diversity of microbial life on Earth. However, the majority of taxa are part of the yet-uncultured microbial dark matter that significantly contributes to ecosystem functioning [140,141].
The data (Table 1, Table 2 and Table 3) indicate that Euzebya is present across the entire biosphere. The question is whether their species were dispersed from marine sources to the terrestrial environment or if they are truly terrestrial, not yet described, species.
In this review, it is shown that Euzebya and other bacteria can thrive under harsh conditions, such as high concentrations of sodium and/or calcium, high electric conductivity, alkaline pH, and highly variable temperature and water fluctuations. These ecological conditions in the studied terrestrial environments are quasi-extreme.
Unfortunately, the culture media used so far for the isolation of Euzebya failed to reproduce the original conditions of these harsh ecosystems and this could be the reason why strains of Euzebya and other bacteria that inhabit the same niche were not isolated.
This review presents some of the pitfalls and limitations of commonly used culture media and suggests possible solutions to challenges faced in isolating terrestrial Euzebya strains. The importance of combining high-throughput sequencing and cultivation techniques is of the utmost interest for this task. Data on the physicochemical and environmental parameters of the terrestrial ecosystems where Euzebya thrives should be taken into account when designing appropriate culture media.
It is expected that the interest in the biogeochemical role and geographical distribution of Euzebya will promote the optimization of culture media, and in this way, researchers will be able to isolate novel Euzebya species from different terrestrial environments.

Author Contributions

Conceptualization, C.S.-J.; investigation, J.L.G.-P., T.M.-P., V.J., L.L., A.F.-C. and S.S.-M.; writing—review and editing, C.S.-J.; project administration, V.J. and S.S.-M. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Spanish Ministry of Science and Innovation, projects PID2020-114978GB-I00 and PID2019-110603RB-I00, MCIN/AEI/10.13039/501100011033, and ERDF.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

No new data were created.

Acknowledgments

This is a contribution from CSIC Interdisciplinary Thematic Platform Open Heritage: Research and Society (PTI-PAIS).

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Herndl, G.J.; Bayer, B.; Baltar, F.; Reinthaler, T. Prokaryotic life in the deep ocean’s water column. Annu. Rev. Mar. Sci. 2023, 15, 461–483. [Google Scholar]
  2. Debbab, A.; Aly, A.H.; Lin, W.H.; Proksch, P. Bioactive compounds from marine bacteria and fungi. Microb. Biotechnol. 2010, 3, 544–563. [Google Scholar]
  3. Eom, S.-H.; Kim, Y.-M.; Kim, S.-K. Marine bacteria: Potential sources for compounds to overcome antibiotic resistance. Appl. Microbiol. Biotechnol. 2013, 97, 4763–4773. [Google Scholar]
  4. Andryukov, B.; Mikhailov, V.; Besednova, N. The biotechnological potential of secondary metabolites from marine bacteria. J. Mar. Sci. Eng. 2019, 7, 176. [Google Scholar]
  5. Sun, W.; Wu, W.; Liu, X.; Zaleta-Pinet, D.A.; Clark, B.R. Bioactive compounds isolated from marine-derived microbes in China: 2009–2018. Mar. Drugs 2019, 17, 339. [Google Scholar]
  6. Carroll, A.R.; Copp, B.R.; Davis, R.A.; Keyzers, R.A.; Prinsep, M. Marine natural products. Nat. Prod. Rep. 2023, 40, 275. [Google Scholar] [PubMed]
  7. Siro, G.; Donald, L.; Pipite, A. The diversity of deep-sea actinobacteria and their natural products: An epitome of curiosity and drug discovery. Diversity 2023, 15, 30. [Google Scholar]
  8. Wibowo, J.T.; Bayu, A.; Aryati, W.D.; Fernandes, C.; Yanuar, A.; Kijjoa, A.; Putra, M.Y. Secondary metabolites from marine-derived bacteria with antibiotic and antibiofilm activities against drug-resistant pathogens. Mar. Drugs 2023, 21, 50. [Google Scholar] [PubMed]
  9. Subramani, R.; Aalbersberg, W. Culturable rare Actinomycetes: Diversity, isolation and marine natural product discovery. Appl. Microbiol. Biotechnol. 2013, 97, 9291–9321. [Google Scholar]
  10. Dhakal, D.; Pokhrel, A.R.; Shrestha, B.; Sohng, J.K. Marine rare Actinobacteria: Isolation, characterization, and strategies for harnessing bioactive compounds. Front. Microbiol. 2017, 8, 1106. [Google Scholar]
  11. Subramani, R.; Sipkema, D. Marine rare actinomycetes: A promising source of structurally diverse and unique novel natural products. Mar. Drugs 2019, 17, 249. [Google Scholar] [CrossRef] [PubMed]
  12. Gattoni, G.; de la Haba, R.R.; Martín, J.; Reyes, F.; Sánchez-Porro, C.; Feola, A.; Zuchegna, C.; Guerrero-Flores, S.; Varcamonti, M.; Ricca, E.; et al. Genomic study and lipidomic bioassay of Leeuwenhoekiella parthenopeia: A novel rare biosphere marine bacterium that inhibits tumor cell viability. Front. Microbiol. 2023, 13, 1090197. [Google Scholar] [CrossRef] [PubMed]
  13. Wei, B.; Du, A.-Q.; Ying, T.-T.; Hu, G.-A.; Zhou, Z.-Y.; Yu, W.-C.; He, J.; Yu, Y.-L.; Wang, H.; Xu, X.-W. Secondary metabolic potential of Kutzneria. J. Nat. Prod. 2023, 86, 1120–1127. [Google Scholar] [CrossRef] [PubMed]
  14. Kurahashi, M.; Fukunaga, Y.; Sakiyama, Y.; Harayama, S.; Yokota, A. Euzebya tangerina gen. nov., sp. nov., a deeply branching marine actinobacterium isolated from the sea cucumber Holothuria edulis, and proposal of Euzebyaceae fam. nov., Euzebyales ord. nov. and Nitriliruptoridae subclassis nov. Int. J. Syst. Evol. Microbiol. 2010, 60, 2314–2319. [Google Scholar] [CrossRef]
  15. Yin, Q.; Zhang, L.; Song, Z.M.; Wu, Y.; Hu, Z.-L.; Zhang, X.-H.; Zhang, Y.; Yu, M.; Xu, Y. Euzebya rosea sp. nov., a rare actinobacterium isolated from the East China Sea and analysis of two genome sequences in the genus Euzebya. Int. J. Syst. Evol. Microbiol. 2018, 68, 2900–2905. [Google Scholar] [CrossRef] [PubMed]
  16. Jian, S.-L.; Xu, L.; Meng, F.-X.; Sun, C.; Xu, X.-W. Euzebya pacifica sp. nov., a novel member of the class Nitriliruptoria. Int. J. Syst. Evol. Microbiol. 2021, 71, 004864. [Google Scholar] [CrossRef]
  17. Xu, L.; Sun, C.; Huang, M.M.; Wu, Y.-H.; Yuan, C.-Q.; Dai, W.-H.; Ye, K.; Han, B.; Xu, X.-W. Complete genome sequence of Euzebya sp. DY32-46, a marine Actinobacteria isolated from the Pacific Ocean. Mar. Genom. 2019, 44, 65–69. [Google Scholar] [CrossRef]
  18. Cuezva, S.; Fernandez-Cortes, A.; Porca, E.; Pasic, L.; Jurado, V.; Hernandez-Marine, M.; Serrano-Ortiz, P.; Cañaveras, J.C.; Sanchez-Moral, S.; Saiz-Jimenez, C. The biogeochemical role of Actinobacteria in Altamira Cave, Spain. FEMS Microbiol. Ecol. 2012, 81, 281–290. [Google Scholar] [CrossRef]
  19. Riquelme, C.; Hathaway, J.J.M.; Dapkevicius, M.L.N.E.; Miller, A.Z.; Kooser, A.; Northup, D.E.; Jurado, V.; Fernandez, O.; Saiz-Jimenez, C.; Cheeptham, N. Actinobacterial diversity in volcanic caves and associated geomicrobiological interactions. Front. Microbiol. 2015, 6, 1342. [Google Scholar] [CrossRef]
  20. Spilde, M.N.; Northup, D.E.; Caimi, N.A.; Boston, P.J.; Stone, F.D.; Smith, S. Microbial Mat Communities in Hawaiian Lava Caves. In International Symposium on Vulcanospeleology 2016; 2016. Available online: http://www.cavepics.com/IVS17/SPILDE.pdf (accessed on 1 June 2023).
  21. Yun, Y.; Wang, H.; Man, B.; Xiang, X.; Zhou, J.; Qiu, X.; Duan, Y.; Engel, A.S. The relationship between pH and bacterial communities in a single karst ecosystem and its implication for soil acidification. Front. Microbiol. 2016, 7, 1955. [Google Scholar] [CrossRef]
  22. Lepinay, C.; Mihajlovski, A.; Seyer, D.; Touron, S.; Bousta, F.; Di Martino, P. Biofilm communities survey at the areas of salt crystallization on the walls of a decorated shelter listed at UNESCO World cultural Heritage. Int. Biodeter. Biodegr. 2017, 122, 116–127. [Google Scholar] [CrossRef]
  23. Itcus, C.; Pascu, M.D.; Lavin, P.; Persoiu, A.; Iancu, L.; Purcarea, C. Bacterial and archaeal community structures in perennial cave ice. Sci. Rep. 2018, 8, 15671. [Google Scholar] [CrossRef] [PubMed]
  24. Gonzalez-Pimentel, J.L.; Miller, A.Z.; Jurado, V.; Laiz, L.; Pereira, M.F.C.; Saiz-Jimenez, C. Yellow colored mats from lava tube of La Palma (Canary Islands, Spain) are dominated by metabolically active Actinobacteria. Sci. Rep. 2018, 8, 1944. [Google Scholar] [CrossRef]
  25. De, A.K.; Muthiyan, R.; Sunder, J.; Bhattacharya, B.; Kundu, A.; Roy, S.D. Profiling bacterial diversity of B2 cave, a limestone cave of Baratang, Andaman and Nicobar Islands, India. Proc. Indian Nat. Sci. Acad. 2019, 85, 853–862. [Google Scholar]
  26. González-Pimentel, J.L. Microorganismos de las Cuevas Volcánicas de La Palma (Islas Canarias): Diversidad y Potencial uso Biotecnológico. Ph.D. Thesis, Universidad Pablo de Olavide, Sevilla, Spain, 2019. [Google Scholar]
  27. Li, M.; Fang, C.; Kawasaki, S.; Huang, M.; Achal, V. Bio-consolidation of cracks in masonry cement mortars by Acinetobacter sp. SC4 isolated from a karst cave. Int. Biodeter. Biodegr. 2019, 141, 94–100. [Google Scholar] [CrossRef]
  28. Luis-Vargas, M.N.; López-Martínez, R.A.; Vilchis-Nestor, A.R.; Daza, R.; Alcántara-Hernández, R.J. Bacterial insights into the formation of opaline stromatolites from the Chimalacatepec lava tube system, Mexico. Geomicrobiol. J. 2019, 36, 694–704. [Google Scholar] [CrossRef]
  29. Frazier, V.E. Carbon Metabolism in Cave Subaerial Biofilms. Master’s Thesis, University of Tennessee, Knoxville, TN, USA, 2020. [Google Scholar]
  30. Miller, A.Z.; García-Sánchez, A.M.; Coutinho, M.L.; Pereira, M.F.C.; Gázquez, F.; Calaforra, J.M.; Forti, P.; Martínez-Frías, J.; Toulkeridis, T.; Caldeira, A.T.; et al. Colored microbial coatings in show caves from the Galapagos Islands (Ecuador): First microbiological approach. Coatings 2020, 10, 1134. [Google Scholar] [CrossRef]
  31. Iquebal, M.A.; Passari, A.K.; Jagannadham, J.; Ahmad, F.; Leo, V.V.; Singh, G.; Jaiswal, S.; Rai, A.; Kumar, D.; Singh, B.P. Microbiome of Pukzing Cave in India shows high antimicrobial activity against plant and animal pathogens. Genomics 2021, 113, 4098–4108. [Google Scholar] [CrossRef]
  32. González-Riancho Fernández, C. Análisis Descriptivo y Funcional de las Colonias Microbianas Visibles que Crecen en la Cueva de Altamira, Enfocado al Diseño de Medidas de Control. Ph.D. Thesis, Universidad de Cantabria, Santander, Spain, 2021. [Google Scholar]
  33. Ma, L.; Huang, X.; Wang, H.; Yun, Y.; Cheng, X.; Liu, D.; Lu, X.; Qiu, X. Microbial interactions drive distinct taxonomic and potential metabolic responses to habitats in karst cave ecosystem. Microbiol. Spectr. 2021, 9, e01152-21. [Google Scholar] [CrossRef] [PubMed]
  34. Weng, M.M.; Zaikova, E.; Millan, M.; Williams, A.J.; McAdam, A.C.; Knudson, C.A.; Fuqua, S.R.; Wagner, N.Y.; Craft, K.; Nawotniak, S.K.; et al. Life underground: Investigating microbial communities and their biomarkers in Mars-analog lava tubes at Craters of the Moon National Monument and Preserve. J. Geophys. Res. Planets 2022, 127, e2022JE007268. [Google Scholar] [CrossRef]
  35. Yi, Y.-J.; Kim, S.-I.; Ahn, U.-S.; Lee, K.C.; Lee, M.-K.; Lee, J.-S.; Kim, D.-S.; Kim, J.-S. Hex code-based geological cross-sections describing landscape dynamics in the Jeju Geomunoreum lava tube system. Korean J. Environ. Agric. 2022, 41, 65–70. [Google Scholar] [CrossRef]
  36. Martín Pozas, T. Papel de los Microorganismos en Procesos de Captación y Emisión de Gases de Efecto Invernadero en Ambientes Subterráneos. Ph.D. Thesis, Universidad Complutense, Madrid, Spain, 2023. [Google Scholar]
  37. Miller, A.Z.; De la Rosa, J.M.; Jiménez-Morillo, N.T.; Pereira, M.F.C.; Gonzalez-Perez, J.A.; Knicker, H.; Saiz-Jimenez, C. Impact of wildfires on subsurface volcanic environments: New insights into speleothem chemistry. Sci. Total Environ. 2020, 698, 134321. [Google Scholar] [CrossRef] [PubMed]
  38. Barton, H.A.; Jurado, V. What’s up down there? Microbial diversity in caves. Microbe 2007, 2, 132–138. [Google Scholar]
  39. Paul, V.G.; Mormile, M.R. A case for the protection of saline and hypersaline environments: A microbiological perspective. FEMS Microbiol. Ecol. 2017, 93, fix091. [Google Scholar] [CrossRef]
  40. Castro-Silva, C.; Ruíz-Valdiviezo, V.M.; Valenzuela-Encinas, C.; Alcántara-Hernández, R.J.; Navarro-Noya, Y.E.; Vázquez-Núñez, E.; Luna-Guido, M.; Marsch, R.; Dendooven, L. The bacterial community structure in an alkaline saline soil spiked with anthracene. Electron. J. Biotechnol. 2013, 16, 10. [Google Scholar]
  41. Yan, H.; Hu, J.; Long, X.; Liu, Z.; Rengel, Z. Salinity altered root distribution and increased diversity of bacterial communities in the rhizosphere soil of Jerusalem artichoke. Sci. Rep. 2016, 6, 20687. [Google Scholar]
  42. De León-Lorenzana, A.S.; Delgado-Balbuena, L.; Domínguez-Mendoza, C.A.; Navarro-Noya, Y.E.; Luna-Guido, M.; Dendooven, L. Soil salinity controls relative abundance of specific bacterial groups involved in the decomposition of maize plant residues. Front. Ecol. Evol. 2018, 6, 51. [Google Scholar] [CrossRef]
  43. Mukhtar, S.; Mirza, B.S.; Mehnaz, S.; Mirza, M.S.; Mclean, J.; Malik, K.A. Impact of soil salinity on the microbial structure of halophyte rhizosphere microbiome. World J. Microbiol. Biotechnol. 2018, 34, 136. [Google Scholar] [CrossRef]
  44. Martínez-Olivas, M.A.; Jiménez-Bueno, N.G.; Hernández-García, J.A.; Fusaro, C.; Luna-Guido, M.; Navarro-Noya, Y.E.; Dendooven, L. Bacterial and archaeal spatial distribution and its environmental drivers in an extremely haloalkaline soil at the landscape scale. PeerJ 2019, 7, e6127. [Google Scholar] [CrossRef]
  45. Sánchez-Sánchez, J.; Cerca, M.; Alcántara-Hernández, R.J.; Lozano-Flores, C.; Carreón-Freyre, D.; Levresse, G.; Vega, M.; Varela-Echavarría, A.; Aranda-Gómez, J.J. Extant microbial communities in the partially desiccated Rincon de Parangueo maar crater lake in Mexico. FEMS Microbiol. Ecol. 2019, 95, fiz051. [Google Scholar] [CrossRef]
  46. Ibarra-Sánchez, C.L.; Pince, L.; Aguirre-Noyola, J.L.; Sánchez-Cerda, K.E.; Navaro-Noya, Y.E.; Luna-Guido, M.; Conde-Barajas, E.; Dendooven, L.; Gomez-Acata, E.S. The microbial community in an alkaline saline sediment of a former maar lake bed. J. Soils Sediments 2020, 20, 542–555. [Google Scholar] [CrossRef]
  47. Wu, N.; Li, Z.; Wu, F.; Tang, M. Microenvironment and microbial community in the rhizosphere of dioecious Populus cathayana at Chaka Salt Lake. J. Soils Sediments 2019, 19, 2740–2751. [Google Scholar] [CrossRef]
  48. Baeshen, M.N.; Moussa, T.A.A.; Ahmed, F.; Abulfaraj, A.A.; Jalal, R.S.; Majaeed, M.A.; Baeshen, N.A.; Huelsenbeck, J.P. Diversity profiling of associated bacteria from the soils of stress tolerant plants from seacoast of Jeddah, Saudi Arabia. Appl. Ecol. Environ. Res. 2020, 18, 8217–8231. [Google Scholar] [CrossRef]
  49. Camacho-Sanchez, M.; Barcia-Piedras, J.M.; Redondo-Gómez, S.; Camacho, M. Mediterranean seasonality and the halophyte Arthrocnemum macrostachyum determine the bacterial community in salt marsh soils in Southwest Spain. Appl. Soil Ecol. 2020, 151, 103532. [Google Scholar] [CrossRef]
  50. Gao, W.; Xu, J.; Zhao, J.; Zhang, H.; Ni, Y.; Zhao, B.; Tebbe, C.C.; Zhang, J.; Jia, Z. Prokaryotic community assembly after 40 years of soda solonetz restoration by natural grassland and reclaimed farmland. Eur. J. Soil Biol. 2020, 100, 103213. [Google Scholar] [CrossRef]
  51. Xu, J.; Gao, W.; Zhao, B.; Chen, M.; Ma, L.; Jia, Z.; Zhang, J. Bacterial community composition and assembly along a natural sodicity/salinity gradient in surface and subsurface soils. Appl. Soil Ecol. 2021, 157, 103731. [Google Scholar] [CrossRef]
  52. Chang, C.; Tian, L.; Tian, Z.; McLaughlin, N.; Tian, C. Change of soil microorganism communities under saline-sodic land degradation on the Songnen Plain in northeast China. J. Plant Nutr. Soil Sci. 2022, 185, 297–307. [Google Scholar] [CrossRef]
  53. Du, X.; Wang, S.; Huang, H.; Zhang, Y.; Ren, X.; Hu, S. Fermenting straw reduced salt damage and improved the stability of the bacterial community in a saline–sodic soil. J. Agric. Sci. Agrotechnol. 2022, 1, 1–18. [Google Scholar] [CrossRef]
  54. Peng, M.; Wang, C.; Wang, Z.; Huang, X.; Zhou, F.; Yan, S.; Liu, X. Differences between the effects of plant species and compartments on microbiome composition in two halophyte Suaeda species. Bioengineered 2022, 13, 12475–12488. [Google Scholar] [CrossRef]
  55. Urana, R.; Yadav, J.; Panchal, S.; Sharma, P.; Singh, N. Phytoremediation of PAH compounds by microbial communities in sodic soil. Int. J. Phytoremediation 2023, 25, 1501–1509. [Google Scholar] [CrossRef]
  56. Chen, D.-D.; Tian, Y.; Jiao, J.-Y.; Zhang, X.-T.; Zhang, Y.-G.; Dong, Z.-Y.; Xiong, M.-J.; Xiao, M.; Shu, W.-S.; Li, W.-J. Comparative genomics analysis of Nitriliruptoria reveals the genomic differences and salt adaptation strategies. Extremophiles 2020, 24, 249–264. [Google Scholar] [CrossRef] [PubMed]
  57. Kurapova, A.I.; Zenova, G.M.; Sudnitsyn, I.I.; Kizilova, A.K.; Manucharova, N.A.; Novrovsuren, Z.H.; Zvyagintsev, D.G. Thermotolerant and thermophilic actinomycetes from soils of Mongolia desert steppe zone. Microbiology 2012, 81, 98–108. [Google Scholar] [CrossRef]
  58. Mohammadipanah, F.; Wink, J. Actinobacteria from arid and desert habitats: Diversity and biological activity. Front. Microbiol. 2016, 6, 1541. [Google Scholar] [CrossRef] [PubMed]
  59. Gacem, M.A.; Ould-El-Hadj-Khelil, A.; Abd-Elsalam, K.A.; Wink, J. Actinobacteria in the Algerian Sahara: Diversity, adaptation mechanism and special unexploited biotopes for the isolation of novel rare taxa. Biologia 2021, 76, 3787–3799. [Google Scholar] [CrossRef]
  60. Hui, M.L.-Y.; Tan, L.T.-H.; Letchumanan, V.; He, Y.-W.; Fang, C.-M.; Chan, K.-G.; Law, J.W.-F.; Lee, L.-H. The extremophilic Actinobacteria: From microbes to medicine. Antibiotics 2021, 10, 682. [Google Scholar] [CrossRef] [PubMed]
  61. Van Goethem, M.W.; Makhalanyane, T.P.; Valverde, A.; Cary, S.C.; Cowan, D.A. Characterization of bacterial communities in lithobionts and soil niches from Victoria Valley, Antarctica. FEMS Microbiol. Ecol. 2016, 92, fiw051. [Google Scholar] [CrossRef]
  62. Meslier, V.; Casero, M.C.; Dailey, M.; Wierzchos, J.; Ascaso, C.; Artieda, O.; McCullough, P.R.; DiRuggiero, J. Fundamental drivers for endolithic microbial community assemblies in the hyperarid Atacama Desert. Environ. Microbiol. 2018, 20, 1765–1781. [Google Scholar] [CrossRef]
  63. Lee, K.C.; Caruso, T.; Archer, S.D.J.; Gillman, L.N.; Lau, M.C.Y.; Cary, S.C.; Lee, C.K.; Pointing, S.B. Stochastic and deterministic effects of a moisture gradient on soil microbial communities in the McMurdo Dry Valleys of Antarctica. Front. Microbiol. 2018, 9, 2619. [Google Scholar] [CrossRef]
  64. Rego, A.; Raio, F.; Martins, T.P.; Ribeiro, H.; Sousa, A.G.G.; Séneca, J.; Baptista, M.S.; Lee, C.K.; Cary, S.C.; Ramos, V.; et al. Actinobacteria and cyanobacteria diversity in terrestrial Antarctic microenvironments evaluated by culture-dependent and independent methods. Front. Microbiol. 2019, 10, 1018. [Google Scholar] [CrossRef]
  65. Araujo, R.; Gupta, V.V.S.R.; Reith, F.; Bisset, A.; Mele, P.; Franco, C.M.M. Biogeography and emerging significance of Actinobacteria in Australia and Northern Antarctica soils. Soil Biol. Biochem. 2020, 146, 107805. [Google Scholar] [CrossRef]
  66. Miralles, I.; Soria, R.; Lucas-Borja, M.E.; Soriano, M.; Ortega, R. Effect of biocrusts on bacterial community composition at different soil depths in Mediterranean semi-arid ecosystems. Sci. Total Environ. 2020, 733, 138613. [Google Scholar] [CrossRef]
  67. Bona, E.; Massa, N.; Toumatia, O.; Novello, G.; Cesaro, P.; Todeschini, V.; Boatti, L.; Mignone, F.; Titouah, H.; Zitouni, A.; et al. Climatic zone and soil properties determine the biodiversity of the soil bacterial communities associated to native plants from desert areas of North-Central Algeria. Microorganisms 2021, 9, 1359. [Google Scholar] [CrossRef]
  68. Khomutovska, N.; de los Ríos, A.; Syczewski, M.D.; Jasser, I. Connectivity of edaphic and endolithic microbial niches in cold mountain desert of Eastern Pamir (Tajikistan). Biology 2021, 10, 314. [Google Scholar] [CrossRef] [PubMed]
  69. Ortiz, M.; Leung, P.M.; Shelley, G.; Jirapanjawat, T.; Nauer, P.A.; Van Goethem, M.W.; Bay, S.K.; Islam, Z.F.; Jordaan, K.; Vikram, S.; et al. Multiple energy sources and metabolic strategies sustain microbial diversity in Antarctic desert soils. Proc. Natl. Acad. Sci. USA 2021, 118, e2025322118. [Google Scholar] [CrossRef] [PubMed]
  70. Osman, J.R.; Wang, Y.; Jaubert, C.; Nguyen, T.-N.; Fernandes, G.R.; DuBow, M.S. The bacterial communities of surface soils from desert sites in the eastern Utah (USA) portion of the Colorado Plateau. Microbiol. Res. 2021, 244, 126664. [Google Scholar] [CrossRef]
  71. Sun, X.; Pei, J.; Zhao, L.; Ahmad, B.; Huang, L.-F. Fighting climate change: Soil bacteria communities and topography play a role in plant colonization of desert areas. Environ. Microbiol. 2021, 23, 6876–6894. [Google Scholar] [CrossRef]
  72. Li, Y.; He, X.; Yuan, H.; Lv, G. Differed growth stage dynamics of root-associated bacterial and fungal community structure associated with halophytic plant Lycium ruthenicum. Microorganisms 2022, 10, 1644. [Google Scholar] [CrossRef] [PubMed]
  73. Sun, J.; Zhang, Q.; Zhou, J.; Wei, Q. Pyrosequencing technology reveals the impact of different manure doses on the bacterial community in apple rhizosphere soil. Appl. Soil Ecol. 2014, 78, 28–36. [Google Scholar] [CrossRef]
  74. Jiménez Bueno, N.G. Efecto de las Diferentes Prácticas de Agricultura Sobre las Comunidades Bacterianas en Suelos del Valle del Yaqui. Ph.D. Thesis, Centro de Investigación y de Estudios Avanzados del Instituto Politécnico Nacional, Mexico City, Mexico, 2016. [Google Scholar]
  75. Lee, H.-J.; Han, S.-I.; Whang, K.-S. Phylogenetic characteristics of actinobacterial population in bamboo (Sasa borealis) soil. Korean J. Microbiol. 2016, 52, 59–64. [Google Scholar] [CrossRef]
  76. Echeverría Molinar, A. Efecto de Factores Abióticos y Bióticos Sobre la Estructura de la Comunidad Microbiana del Suelo en un Ambiente Oligotrófico. Master’s Thesis, Instituto Potosino de Investigación Científica y Tecnológica, San Luis Potosí, Mexico, 2017. [Google Scholar]
  77. Wolinska, A.; Görniak, D.; Zielenkiewicz, U.; Kuzniar, A.; Izak, D.; Banach, A.; Blaszczyk, M. Actinobacteria structure in autogenic, hydrogenic and lithogenic cultivated and non-cultivated soils: A culture-independent approach. Agronomy 2019, 9, 598. [Google Scholar] [CrossRef]
  78. Liu, C.; Zhao, X.; Lin, Q.; Li, G. Decrease in diversity and shift in composition of the soil bacterial community were closely related to high available phosphorus in agricultural Fluvisols of North China. Acta Agric. Scand. Soil Plant Sci. 2019, 69, 618–630. [Google Scholar] [CrossRef]
  79. An, Z.; Guo, F.; Chen, Y.; Bai, G.; Chen, Z. Rhizosphere bacterial and fungal communities during the growth of Angelica sinensis seedlings cultivated in an Alpine uncultivated meadow soil. PeerJ 2020, 8, e8541. [Google Scholar] [CrossRef] [PubMed]
  80. Biderre-Petit, C.; Hochart, C.; Gardon, H.; Dugat-Bony, E.; Terrat, S.; Jouan-Dufournel, I.; Paris, R. Analysis of bacterial and archaeal communities associated with Fogo volcanic soils of different ages. FEMS Microbiol. Ecol. 2020, 96, fiaa104. [Google Scholar] [CrossRef] [PubMed]
  81. López-Lozano, N.E.; Echeverría Molinar, A.; Ortiz Durán, E.A.; Hernández Rosales, M.; Souza, V. Bacterial diversity and interaction networks of Agave lechuguilla rhizosphere differ significantly from bulk soil in the oligotrophic basin of Cuatro Cienegas. Front. Plant Sci. 2020, 11, 1028. [Google Scholar] [CrossRef] [PubMed]
  82. Cui, Y.; Yong, L.; Rongli, M.; Wen, D.; Zhixian, Z.; Xingming, H. Metagenomics analysis of the effects of long-term stand age on beneficial soil bacterial community structure under Chinese ancient mulberry farming practice. Hortic. Environ. Biotechnol. 2020, 61, 1063–1071. [Google Scholar] [CrossRef]
  83. Lopes, L.S.; Mendes, L.W.; Antunes, J.E.L.; Oliverira, L.M.S.; Melo, V.M.M.; Pereira, A.P.A.; Costa, A.F.; Oliveira, J.P.; Martínez, C.R.; Figueiredo, M.V.B.; et al. Distinct bacterial community structure and composition along different cowpea producing ecoregions in Northeastern Brazil. Sci. Rep. 2021, 11, 831. [Google Scholar] [CrossRef]
  84. Hazzouri, K.M.; Sudalaimuthuasari, N.; Saeed, E.E.; Kundu, B.; Al-Maskari, R.S.; Nelson, D.; AlShehhi, A.A.; Aldhuhoori, M.A.; Almutawa, D.S.; Alshehhi, F.R.; et al. Salt flat microbial diversity and dynamics across salinity gradient. Sci. Rep. 2022, 12, 11293. [Google Scholar] [CrossRef]
  85. Liu, A.; Li, Y.; Wang, Q.; Zhang, X.; Xiong, J.; Li, Y.; Lei, Y.; Sun, Y. Analysis of microbial diversity and community structure of rhizosphere soil of Cistanche salsa from different host plants. Front. Microbiol. 2022, 13, 971228. [Google Scholar] [CrossRef]
  86. Pino-Otín, M.R.; Ferrando, N.; Ballestero, D.; Langa, E.; Roig, F.J.; Terrado, E.M. Impact of eight widely consumed antibiotics on the growth and physiological profile of natural soil microbial communities. Chemosphere 2022, 305, 135473. [Google Scholar] [CrossRef]
  87. Wang, L.; Peng, C.; Gong, B.; Yang, Z.; Song, J.; Li, L.; Xu, L.; Yue, T.; Wang, X.; Yang, M.; et al. Actinobacteria community and their antibacterial and cytotoxic activity on the Weizhou and Xieyang volcanic islands in the Beibu Gulf of China. Front. Microbiol. 2022, 13, 911408. [Google Scholar] [CrossRef]
  88. Weels, S.S.L.; Welz, P.J.; Prins, A.; Le Roes-Hill, M. Impact of physicochemical parameters on the diversity and distribution of microbial communities associated with three South African peatlands. Microorganisms 2022, 10, 2103. [Google Scholar] [CrossRef] [PubMed]
  89. Baldi, D.S.; Humphrey, C.E.; Kyndt, J.A.; Moore, T.C. Native plant gardens support more microbial diversity and higher relative abundance of potentially beneficial taxa compared to adjacent turf grass lawns. Urban Ecosyst. 2023, 26, 807–820. [Google Scholar] [CrossRef]
  90. David, A.B.; Mwaikomo, K.S.; Midega, C.; Magingo, F.; Alsanius, B.W.; Drinkwater, L.E.; Dekker, T.; Lyantagaye, S. A comparative study on the impact of five Desmodium species on soil microbiome reveals enrichment of selected bacterial and fungal taxa. bioRxiv 2023. [Google Scholar] [CrossRef]
  91. Duan, M.; Wang, L.; Song, X.; Zhang, X.; Wang, Z.; Lei, J.; Yan, M. Assessment of the rhizosphere fungi and bacteria recruited by sugarcane during smut invasion. Braz. J. Microbiol. 2023, 54, 385–395. [Google Scholar] [CrossRef] [PubMed]
  92. Cheng, Y.; Xie, X.; Wang, X.; Zhu, L.; Qiu, Q.-S.; Xu, X. Effects of the salt-tolerant gramineous forage Echinochloa frumentacea on biological improvement and crop productivity in saline–alkali land on the Hetao Ningxia Plain in China. Sustainability 2023, 15, 5319. [Google Scholar] [CrossRef]
  93. Manucharova, N.A.; Kovalenko, M.A.; Alekseeva, M.G.; Babenko, A.D.; Stepanov, A.L. Biotechnological potential of hydrolytic prokaryotic component in soils. Eurasian Soil Sci. 2023, 56, 558–572. [Google Scholar] [CrossRef]
  94. Wang, Y.; Wang, Y.; Zhang, Q.; Fan, H.; Wang, X.; Wang, J.; Zhou, Y.; Chen, Z.; Sun, F.; Cui, X. Saline-alkali soil property improved by the synergistic effects of Priestia aryabhattai JL-5, Staphylococcus pseudoxylosus XW-4, Leymus chinensis and soil microbiota. Int. J. Mol. Sci. 2023, 24, 7737. [Google Scholar] [CrossRef]
  95. Wang, D.; Ren, H. Microbial community in buckwheat rhizosphere with different nitrogen application rates. PeerJ 2023, 11, e15514. [Google Scholar] [CrossRef]
  96. Peng, M.; Zi, X.; Wang, Q. Bacterial community diversity of oil-contaminated soils assessed by high throughput sequencing of 16S rRNA genes. Int. J. Environ. Res. Public Health 2015, 12, 12002–12015. [Google Scholar] [CrossRef]
  97. Kumar, V.; AlMomin, S.; Al-Aqeel, H.; Al-Salameen, F.; Nair, S.; Shajan, A. Metagenomic analysis of rhizosphere microflora of oil-contaminated soil planted with barley and alfalfa. PLoS ONE 2018, 13, e0202127. [Google Scholar] [CrossRef]
  98. Ke, W.; Zhang, X.; Zhu, F.; Wu, H.; Zhang, Y.; Shi, Y.; Hartley, W.; Xue, S. Appropriate human intervention stimulates the development of microbial communities and soil formation at a long-term weathered bauxite residue disposal area. J. Hazard. Mater. 2021, 405, 124689. [Google Scholar] [PubMed]
  99. Rahman, K.M.J.; Diba, F.; Shuvo, M.S.R.; Siddique, M.A.; Hossain, M.A.; Sultana, M. Metagenomic investigation of bacterial community of arsenic-prone area in the northwest region of Bangladesh. Bangladesh J. Microbiol. 2022, 39, 31–38. [Google Scholar] [CrossRef]
  100. Ossanna, L.Q.R.; Serrano, K.; Jennings, L.L.; Dillon, J.; Maier, R.M.; Neilson, J.W. Progressive belowground soil development associated with sustainable plant establishment during copper mine waste revegetation. Appl. Soil Ecol. 2023, 186, 104813. [Google Scholar] [CrossRef]
  101. Feng, G.; Yong, J.; Liu, Q.; Chen, H.; Hu, Y.; Mao, P. Remedial effect and operating status of a decommissioned uranium mill tailings (UMT) repository: A micro-ecological perspective based on bacterial community. J. Environ. Manag. 2023, 340, 117993. [Google Scholar]
  102. Akatova, E. Estudio Comparativo de las Comunidades Microbianas en las Tumbas de la Necrópolis de Carmona Basado en Técnicas de Biología Molecular. Ph.D. Thesis, Universidad de Sevilla, Sevilla, Spain, 2009. [Google Scholar]
  103. Héry, M.; Rizoulis, A.; Sanguin, H.; Cooke, D.A.; Pancost, R.D.; Polya, D.A.; Lloyd, J.R. Microbial ecology of arsenic-mobilizing Cambodian sediments: Lithological controls uncovered by stable-isotope probing. Environ. Microbiol. 2014, 17, 1857–1869. [Google Scholar] [CrossRef]
  104. Mirete, S.; Mora-Ruiz, M.R.; Lamprecht-Grandío, M.; de Figueras, C.G.; Rosselló-Móra, R.; González-Pastor, J.E. Salt resistance genes revealed by functional metagenomics from brines and moderate-salinity rhizosphere within a hypersaline environment. Front. Microbiol. 2015, 6, 1121. [Google Scholar]
  105. Ivanova, E.A.; Pershina, E.V.; Kutovaya, O.V.; Sergaliev, N.K.h.; Nagieva, A.G.; Zhiengaliev, A.T.; Provorov, N.A.; Andronov, E.E. Comparative analysis of microbial communities of contrasting soil types in different plant communities. Russ. J. Ecol. 2018, 49, 30–39. [Google Scholar] [CrossRef]
  106. Truchado, P.; Gil, M.I.; Suslow, T.; Allende, A. Impact of chlorine dioxide disinfection of irrigation water on the epiphytic bacterial community of baby spinach and underlying soil. PLoS ONE 2018, 13, e0199291. [Google Scholar]
  107. West, N.J.; Parrot, D.; Fayet, C.; Grube, M.; Tomasi, S.; Suzuki, M.T. Marine cyanolichens from different littoral zones are associated with distinct bacterial communities. PeerJ 2018, 6, e5208. [Google Scholar]
  108. Dyda, M.; Pyzik, A.; Wilkojc, E.; Kwiatkowska-Kopka, B.; Sklodowska, A. Bacterial and fungal diversity inside the medieval building constructed with sandstone plates and lime mortar as an example of the microbial colonization of a nutrient-limited extreme environment (Wawel Royal Castle, Krakow, Poland). Microorganisms 2019, 7, 416. [Google Scholar] [CrossRef]
  109. Hernández, E.A.; Lopez, J.L.; Piquet, A.M.-T.; Mac Cormack, W.P.; Buma, A.G.J. Changes in salinity and temperature drive marine bacterial communities’ structure at Potter Cove, Antarctica. Polar Biol. 2019, 42, 2177–2191. [Google Scholar]
  110. Povedano-Priego, C.; Jroundi, F.; Lopez-Fernandez, M.; Sánchez-Castro, I.; Martín-Sánchez, I.; Huertas, J.; Merroun, M.L. Shifts in bentonite bacterial community and mineralogy in response to uranium and glicerol-2-phosphate exposure. Sci. Total Environ. 2019, 692, 219–232. [Google Scholar] [PubMed]
  111. Feby, A.; Divya, B.; Nair, S. Bacterial diversity in demosponges from the coral reefs of Lakshadweep, India. Rom. J. Biol. Zool. 2021, 66, 85–100. [Google Scholar]
  112. Ephraim, E.; Brockman, J.A.; Jewell, D.E. A diet supplemented with polyphenols, prebiotics and omega-3 fatty acids modulates the intestinal microbiota and improves the profile of metabolites linked with anxiety in dogs. Biology 2022, 11, 976. [Google Scholar] [PubMed]
  113. Li, C.; Liu, J.; Chen, X.; Ren, H.; Su, B.; Ma, K.; Tu, Q. Determinism governs the succession of disturbed bacterioplankton communities in a coastal maricultural ecosystem. Sci. Total Environ. 2022, 828, 154457. [Google Scholar] [PubMed]
  114. Marchywka, M. Clinical and Microbiological Improvement in Dog after Metal and Benzoate Containing Supplement Mix; Tech Report MJM-2022-013; Public Note: Austin, TX, USA, 2022. [Google Scholar] [CrossRef]
  115. Niemiec, B.A.; Gawor, J.; Tang, S.; Prem, A.; Krumbeck, J.A. The bacteriome of the oral cavity in healthy dogs and dogs with periodontal disease. Am. J. Vet. Res. 2022, 83, 50–58. [Google Scholar]
  116. Richter, H.E.; Carnes, M.U.; Komesu, Y.M.; Lukacz, E.S.; Arya, L.; Bradley, M.; Rogers, R.G.; Sung, V.W.; Siddiqui, N.Y.; Carper, B.; et al. Association between the urogenital microbiome and surgical treatment response in women undergoing midurethral sling operation for mixed urinary incontinence. Am. J. Obstet. Gynecol. 2022, 226, 93.e1–93.e15. [Google Scholar]
  117. Chen, B.-Y.; Lin, W.-Z.; Li, Y.-L.; Bi, C.; Du, L.-J.; Liu, Y.; Zhou, L.-J.; Liu, T.; Xu, S.; Shi, C.-J.; et al. Roles of oral microbiota and oral-gut microbial transmission in hypertension. J. Adv. Res. 2023, 43, 147–161. [Google Scholar]
  118. Fan, S.; He, X.; Zhu, Z.; Chen, L.; Zou, Y.; Chen, Z.; Yu, J.; Chen, W.; Guan, H.; Ma, J. Integrating host transcriptomic signatures for distinguishing autoimmune encephalitis in cerebrospinal fluid by metagenomic sequencing. Cell Biosci. 2023, 13, 111. [Google Scholar]
  119. Parab, A.S.; Manohar, C.S.; Ghose, M.P. Influence of seasonal variations in primary productivity on the bacterial community structure at Chlorophyll Maximum (C-Max) depths along the west coast of India. bioRxiv 2023. [Google Scholar] [CrossRef]
  120. Nieto, J.J. The response of halophilic bacteria to heavy metals. In General and Applied Aspects of Halophilic Microorganisms; Rodriguez-Valera, F., Ed.; Plenum Press: New York, NY, USA, 1991; pp. 173–179. [Google Scholar]
  121. Voica, D.M.; Bartha, L.; Banciu, H.L.; Oren, A. Heavy metal resistance in halophilic Bacteria and Archaea. FEMS Microbiol. Lett. 2016, 363, fnw146. [Google Scholar] [PubMed]
  122. Sowmya, M.; Hatha, A.A.H. Cadmium and lead tolerance mechanisms in bacteria and the role of halotolerant and moderately halophilic bacteria in their remediation. In Handbook of Metal-Microbe Interactions and Bioremediation; Das, S., Dash, H.R., Eds.; CRC Press: Boca Raton, FL, USA, 2017; pp. 557–573. [Google Scholar]
  123. Amoozegar, M.A.; Hamedi, J.; Dadashipour, M.; Shariatpanahi, S. Effect of salinity on the tolerance to toxic metals and oxyanions in native moderately halophilic spore-forming bacilli. World J. Microbiol. Biotechnol. 2005, 21, 1237–1243. [Google Scholar]
  124. Divakar, G.; Sameer, R.S.; Bapuji, M. Screening of multi-metal tolerant halophilic bacteria for heavy metal remediation. Int. J. Curr. Microbiol. App. Sci. 2018, 7, 2062–2076. [Google Scholar]
  125. Laiz, L.; Miller, A.Z.; Jurado, V.; Akatova, E.; Sanchez-Moral, S.; Gonzalez, J.M.; Dionísio, A.; Macedo, M.F.; Saiz-Jimenez, C. Isolation of Rubrobacter strains from biodeteriorated monuments. Naturwissenschaften 2009, 96, 71–79. [Google Scholar] [PubMed]
  126. Jurado, V.; Miller, A.Z.; Alias-Villegas, C.; Laiz, L.; Saiz-Jimenez, C. Rubrobacter bracarensis sp. nov., a novel member of the genus Rubrobacter isolated from a biodeteriorated monument. Syst. Appl. Microbiol. 2012, 35, 306–309. [Google Scholar]
  127. Martin-Pozas, T.; Gonzalez-Pimentel, J.L.; Jurado, V.; Laiz, L.; Cañaveras, J.C.; Fernandez-Cortes, A.; Cuezva, S.; Sanchez-Moral, S.; Saiz-Jimenez, C. Crossiella, a rare Actinomycetota genus, abundant in the environment. Appl. Biosci. 2023, 2, 194–210. [Google Scholar]
  128. Martin-Pozas, T.; Fernandez-Cortes, A.; Cuezva, S.; Cañaveras, J.C.; Benavente, D.; Duarte, E.; Saiz-Jimenez, C.; Sanchez-Moral, S. New insights into the structure, microbial diversity and ecology of yellow biofilms in a Paleolithic rock art cave (Pindal Cave, Asturias, Spain). Sci. Total Environ. 2023, 897, 165218. [Google Scholar]
  129. Boquet, E.; Boronat, A.; Ramos-Cormenzana, A. Production of calcite (calcium carbonate) crystals by soil bacteria is a general phenomenon. Nature 1973, 246, 527–528. [Google Scholar]
  130. Borodina, E.; Kelly, D.P.; Rainey, F.A.; Ward-Rainey, N.L.; Wood, A.P. Dimethylsulfone as a growth substrate for novel methylotrophic species of Hyphomicrobium and Arthrobacter. Arch. Microbiol. 2000, 173, 425–437. [Google Scholar]
  131. Steven, B.; Briggs, G.; McKay, C.P.; Pollard, W.H.; Greer, C.W.; Whyte, L.G. Characterization of the microbial diversity in a permafrost sample from the Canadian high Arctic using culture-dependent and culture-independent methods. FEMS Microbiol. Ecol. 2007, 59, 513–523. [Google Scholar]
  132. Belov, A.A.; Cheptsov, V.S.; Vorobyova, E.A. Soil bacterial communities of Sahara and Gibson deserts: Physiological and taxonomical characteristics. AIMS Microbiol. 2018, 4, 685–710. [Google Scholar] [CrossRef]
  133. Govil, T.; Paste, M.; Samanta, D.; David, A.; Goh, K.M.; Li, X.; Salem, D.R.; Sani, R.K. Metagenomics and culture dependent insights into the distribution of Firmicutes across two different sample types located in the Black Hills region of South Dakota, USA. Microorganisms 2021, 9, 113. [Google Scholar] [CrossRef]
  134. Molina-Menor, E.; Gimeno-Valero, H.; Pascual, J.; Peretó, J.; Porcar, M. High culturable bacterial diversity from a European desert: The Tabernas Desert. Front. Microbiol. 2021, 11, 583120. [Google Scholar] [CrossRef]
  135. Stefani, F.O.P.; Bell, T.H.; Marchand, C.; de la Providencia, I.E.; El Yassimi, A.; St-Arnaud, M.; Hijri, M. Culture-dependent and –independent methods capture different microbial community fractions in hydrocarbon-contaminated soils. PLoS ONE 2015, 10, e0128272. [Google Scholar]
  136. Vaz-Moreira, I.; Egas, C.; Nunes, O.C.; Manaia, C.M. Culture-dependent and culture-independent diversity surveys target different bacteria: A case study in a freshwater sample. Anton. Leeuw. 2011, 100, 245–257. [Google Scholar] [CrossRef] [PubMed]
  137. Laiz, L.; Piñar, G.; Lubitz, W.; Saiz-Jimenez, C. Monitoring the colonization of monuments by bacteria: Cultivation vs molecular methods. Environ. Microbiol. 2003, 5, 72–74. [Google Scholar] [CrossRef]
  138. Kurahashi, M.; Fukunaga, Y.; Sakiyama, Y.; Harayama, S.; Yokota, A. Iamia majanohamensis gen. nov., sp. nov., an actinobacterium isolated from sea cucumber Holothuria edulis, and proposal of Iamiaceae fam. nov. Int. J. Syst. Evol. Microbiol. 2009, 59, 869–873. [Google Scholar] [CrossRef] [PubMed]
  139. Flores, N.; Hoyos, S.; Venegas, M.; Galetovic, A.; Zúñiga, L.M.; Fábrega, F.; Paredes, B.; Salazar-Ardiles, C.; Vilo, C.; Ascaso, C.; et al. Haloterrigena sp. strain SGH1, a bacterioruberin-rich, perchlorate-tolerant halophilic archaeon isolated from halite microbial communities, Atacama Desert, Chile. Front. Microbiol. 2020, 11, 324. [Google Scholar] [CrossRef]
  140. Jiao, J.-Y.; Liu, L.; Hua, Z.-S.; Fang, B.-Z.; Zhou, E.-M.; Salam, N.; Hedlund, B.P.; Li, W.-J. Microbial dark matter coming to light: Challenges and opportunities. Nat. Sci. Rev. 2021, 8, nwaa280. [Google Scholar] [CrossRef]
  141. Pascoal, F.; Costa, R.; Magalhaes, C. The microbial rare biosphere: Current concepts, methods and ecological principles. FEMS Microbiol. Ecol. 2021, 97, fiaa227. [Google Scholar]
Figure 1. (a) Pink biofilms growing on calcite speleothems in Pindal Cave, Spain (red arrow). (bd) Scanning electron microscopy microphotographs of pink biofilms from Pindal Cave. (b) General view of pink biofilms (red arrow). (c,d) Bacterial filaments forming the biofilm.
Figure 1. (a) Pink biofilms growing on calcite speleothems in Pindal Cave, Spain (red arrow). (bd) Scanning electron microscopy microphotographs of pink biofilms from Pindal Cave. (b) General view of pink biofilms (red arrow). (c,d) Bacterial filaments forming the biofilm.
Applsci 13 09644 g001
Table 1. Occurrence and relative abundance of Euzebyales/Euzebyaceae/Euzebya in caves.
Table 1. Occurrence and relative abundance of Euzebyales/Euzebyaceae/Euzebya in caves.
CaveAbundance %TaxaType of SampleReferences
Altamira Cave, Spainn.a.EuzebyaGrey biofilms[18]
Volcanic caves, Portugal, USAn.a.EuzebyalesBiofilms[19]
Hawai’i lava caves, USAn.a.EuzebyaBiofilms[20]
Heshang Cave, China n.a.EuzebyaWeathered rocks[21]
Laugerie-Haute shelter, France 2.6 *EuzebyaBiofilms[22]
Scarisoara Ice Cave, Romanian.a.EuzebyaIce core[23]
Honda del Bejenado Cave, Spain43.9 *EuzebyaYellow biofilms[24]
B2 Cave, India1.16EuzebyalesCave wall[25]
Honda del Bejenado Cave, Spain31.7EuzebyaYellow biofilms[26]
Fuente de la Canaria Cave, Spain0.2–2.7EuzebyaYellow biofilms/moonmilk[26]
Bucara II Cave, Spain2.9–11.0EuzebyaPink deposit/moonmilk[26]
Llano de los Caños Cave, Spain3.0EuzebyaSpeleothem[26]
Yixing Shanjuan Cave, China4.2EuzebyaSpeleothem[27]
Chimalacatepec lava tube, Mexico6.2EuzebyaStromatolite[28]
RN5 Cave, USA30.7EuzebyaBiofilms[29]
RN5 Cave, USA13.8EuzebyaceaeBiofilms[29]
KN14 Cave, USA0.1EuzebyaBiofilms[29]
Royal Palm Cave, Galapagosn.a.EuzebyaWhite biofilms[30]
Pukzing Cave, Indian.a.EuzebyaCave sediments[31]
Altamira Cave, Spain 33–79EuzebyaceaeWhite biofilms[32]
Altamira Cave, Spain 20–42EuzebyaceaeLight brown biofilms[32]
Heshang Cave, China n.a.EuzebyaWeathered rocks[33]
Moon National Monument, USA n.a.EuzebyaBiofilms/Speleothems[34]
Geomunoreum lava tubes, Korea 0.3–0.7EuzebyaMicrobial mats[35]
Pindal Cave, Spain 7.0–16.0EuzebyaceaePink biofilms[36]
Covadura Cave, Spain 48.4–52.5
0.1–21.7
0.7–10.4
3.4–9.0
Euzebyaceae
Euzebyaceae
Euzebyaceae
Euzebyaceae
White biofilms (2010)
White biofilms (2022)
Yellow biofilms (2010)
Yellow biofilms (2022)
Unpublished report
n.a., data not available. * Abundance of clones.
Table 3. Occurrence of Euzebyales/Euzebyaceae/Euzebya in soils and other diverse environments.
Table 3. Occurrence of Euzebyales/Euzebyaceae/Euzebya in soils and other diverse environments.
LocationTaxaType of Sample References
Soils
Unknown, ChinaEuzebyaSoil/Rhizosphere[73]
Valle del Yaqui, MéxicoEuzebyaSoil[74]
Unknown, KoreaEuzebyaceaeSoil/Rhizosphere[75]
Cuatro Cienegas Basin, MexicoEuzebyaSoil/Rhizosphere[76]
Lublin region, PolandEuzebyaceaeSoil[77]
Beijing, ChinaEuzebyaSoil[78]
Dingxi, ChinaEuzebyaRhizosphere[79]
Fogo Island, Cape VerdeEuzebyaVolcanic soils[80]
Cuatro Cienegas Basin, Mexico EuzebyaSoil/Rhizosphere[81]
Hotan City, Xinjiang Uygur, ChinaEuzebyaSoil[82]
Pernambuco, BrazilEuzebyaceaeSoil[83]
Outside a sabkha, Abu Dhabi EuzebyalesSoil[84]
Qapqal County, Xinjiang, China EuzebyaceaeSoil/Rhizosphere[85]
Zaragoza, Spain EuzebyaSoil[86]
Weizhou and Xieyang Islands, China EuzebyaVolcanic soils[87]
Springfield Farm, Western Cape, South Africa EuzebyaPeatlands[88]
Omaha/Lincoln, Nebraska, USAEuzebyaSoil[89]
International Centre for Insect Physiology, KenyaEuzebyaceaeSoil[90]
Sugarcane Research Institute, Nanning, China,EuzebyaSoil/Rhizosphere[91]
Hetao Ningxia Plain, ChinaEuzebyaSoil/Rhizosphere[92]
Different Russian regions and AntarcticaEuzebyaSoils[93]
Saline–alkali regions, Northeastern ChinaEuzebyaSoil[94]
Jinzhong City, Shanxi Province, China EuzebyaSoil/Rhizosphere[95]
Contaminated soils
Daqing oilfield, ChinaEuzebyaOil polluted soil[96]
KuwaitEuzebyaOil polluted soil[97]
Shandong Province, ChinaEuzebyaBauxite residue[98]
Northwest region of BangladeshEuzebyaAs-polluted soil[99]
Copper mine, Miami, Arizona, USAEuzebyaceaeMine waste rock[100]
Xinjiang, Northwest ChinaEuzebyaU repositories[101]
Diverse environments
Mausoleo Cuadrangular, Carmona, SpainEuzebyaRoman tomb[102]
Cambodian aquiferEuzebyaAs-rich sediments[103]
EsTrenc saltern, Mallorca, SpainEuzebyaBrine/Rhizosphere[104]
Akkol salt lake, RussiaEuzebyaceaeLakeshore [105]
Pozo de la Higuera, Almeria, SpainEuzebyaIrrigation waters[106]
Houssaye Point, Erquy, FranceEuzebyaMarine lichens[107]
Wawel Royal Castle, Krakow, PolandEuzebyaceaeBuilding stones[108]
Potter Cove, AntarcticaEuzebyaSeawater[109]
Bentonite deposit, Almeria, SpainEuzebyaBentonite[110]
Coral reefs, Lakshadweep, IndiaEuzebyaDemosponges[111]
Dogs, USAEuzebyaFeces[112]
Coastal waters, Yantai City, China,EuzebyaBacterioplankton[113]
Dogs, USAEuzebyaVomit[114]
Dogs, USAEuzebyaOral cavity[115]
Human microbiomeEuzebyaUrogenital [116]
Human microbiomeEuzebyaOral cavity[117]
Human microbiomeEuzebyaCerebrospinal fluid[118]
West coast of IndiaEuzebyaSeawater[119]
Table 4. NGS relative abundances (%) of the top five taxa in samples from pink biofilms, Pindal Cave, Spain [36].
Table 4. NGS relative abundances (%) of the top five taxa in samples from pink biofilms, Pindal Cave, Spain [36].
GenusSample Bal1Sample Bal4
Euzebyaceae167
Crossiella87
wb1-P19511
PLTA1345
Nitrospira33
Other genera6467
Table 5. Strains isolated from pink biofilms, Pindal Cave, Spain.
Table 5. Strains isolated from pink biofilms, Pindal Cave, Spain.
StrainCulture MediumIdentification (% Similarity) *Accession Number
R2-11B-4Peribacillus frigoritolerans (100)OR037511
R2-14DimethylsulfoneStreptomyces sp. (99.89)OR037512
R2-15ATSA/1000Streptomyces sp. (99.66)OR037513
R2-15BTSA/1000Micromonospora chalcea (99.77)OR037514
R2-1NABacillus altitudinis (99.89)OR037515
R2-5TSABacillus thuringiensis (100)OR037516
R2-6TSABacillus mojavensis (100)OR037517
R2-8GYM StreptomycesPsychrobacillus vulpis (98.92)OR037518
R4-12B-4Paenibacillus peoriae (99.78)OR037519
R4-13TSA/1000Peribacillus frigoritolerans (100)OR037520
R4-14TSA/1000Streptomyces sp. (99.67)OR037521
R4-15DimethylsulfoneRhodococcus erythropolis (100)OR037522
R4-17DimethylsulfoneRhodococcus koreensis (99.31)OR037523
R4-3GYM StreptomycesPsychrobacillus glaciei (99.77)OR037524
R4-4NAPaenibacillus pabuli (99.78)OR037525
R4-5NABacillus thuringiensis (100)OR037526
R4-6TSAPsychrobacillus vulpis (98.92)OR037527
R4-7TSAPeribacillus sp. (99.03)OR037528
R4-8TSAMetabacillus sediminilitoris (99.03)OR037529
* Closest relative obtained by comparison with the NCBI database.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Gonzalez-Pimentel, J.L.; Martin-Pozas, T.; Jurado, V.; Laiz, L.; Fernandez-Cortes, A.; Sanchez-Moral, S.; Saiz-Jimenez, C. The Marine Bacterial Genus Euzebya Is Distributed Worldwide in Terrestrial Environments: A Review. Appl. Sci. 2023, 13, 9644. https://doi.org/10.3390/app13179644

AMA Style

Gonzalez-Pimentel JL, Martin-Pozas T, Jurado V, Laiz L, Fernandez-Cortes A, Sanchez-Moral S, Saiz-Jimenez C. The Marine Bacterial Genus Euzebya Is Distributed Worldwide in Terrestrial Environments: A Review. Applied Sciences. 2023; 13(17):9644. https://doi.org/10.3390/app13179644

Chicago/Turabian Style

Gonzalez-Pimentel, Jose Luis, Tamara Martin-Pozas, Valme Jurado, Leonila Laiz, Angel Fernandez-Cortes, Sergio Sanchez-Moral, and Cesareo Saiz-Jimenez. 2023. "The Marine Bacterial Genus Euzebya Is Distributed Worldwide in Terrestrial Environments: A Review" Applied Sciences 13, no. 17: 9644. https://doi.org/10.3390/app13179644

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop